SSSAJ
HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
 QUICK SEARCH:   [advanced]


     


Published online 28 June 2005
Published in Soil Sci Soc Am J 69:1225-1232 (2005)
DOI: 10.2136/sssaj2004.0335
© 2005 Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
This Article
Right arrow Abstract Freely available
Right arrow Full Text Free
Right arrow Full Text (PDF) Free
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via Web of Science (4)
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Dontsova, K. M.
Right arrow Articles by Johnston, C. T.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Dontsova, K. M.
Right arrow Articles by Johnston, C. T.
GeoRef
Right arrow GeoRef Citation
Agricola
Right arrow Articles by Dontsova, K. M.
Right arrow Articles by Johnston, C. T.
Related Collections
Right arrow Soil Chemistry

Calcium and Magnesium Effects on Ammonia Adsorption by Soil Clays

Katerina M. Dontsovaa,b,c,*, L. Darrell Nortona,b and Cliff T. Johnstona

a Dep. of Agronomy, Purdue Univ., West Lafayette, IN 47907-1968
b USDA-ARS, National Soil Erosion Research Lab., West Lafayette, IN 47907
c Currently at the Univ. of Mississippi, duty station: U.S. Army Engineer Research and Development Center, 3909 Halls Ferry Rd., Vicksburg, MS 39180



View larger version (23K):

[in a new window]
 
Fig. 1. Schematic diagram of ammonia distribution in the soil. M is metal exchangeable cation; OM—organic matter. Species not present in model clay system are marked in gray.

 


View larger version (27K):

[in a new window]
 
Fig. 2. Change in the weight of the Mg-exchanged Fayette sample as experiment progresses. Dashed vertical lines indicate times at which spectra shown on Fig. 3 were taken.

 


View larger version (27K):

[in a new window]
 
Fig. 3. Fourier transform infrared (FTIR) spectra of dry Fayette Mg sample before ammonia injection (a), immediately after ammonia injection (b), and 25 min after injection (c). Difference between Spectra c and a (d).

 


View larger version (19K):

[in a new window]
 
Fig. 4. Correlation between amount of ammonium adsorbed and water displaced for Blount and Fayette soil clays.

 


View larger version (42K):

[in a new window]
 
Fig. 5. Nitrogen retention in Blount and Fayette soil clays as a function of the exchangeable cation and relative humidity (RH). "Wet" samples were equilibrated at 90% RH, while "dry" were at 2% RH. Significant differences at 0.05 probability level are indicated by the different letters within the same measure: NH+4, NH3, and NH+4 + NH3.

 


View larger version (14K):

[in a new window]
 
Fig. 6. Correlation between ammonium and water content for Blount and Fayette clays, and Fayette without organic matter (OM) at 2% relative humidity. Each point represents one sample.

 


View larger version (46K):

[in a new window]
 
Fig. 7. Effect of organic matter (OM) removal on NH3 sorption by Fayette clay. "Wet" samples were equilibrated at 90% RH, while "dry" were at 2% RH. Significant differences at 0.05 probability level are indicated by the different letters within the same measure: NH+4, NH3, and NH+4 + NH3.

 


View larger version (16K):

[in a new window]
 
Fig. 8. Correlation between ammonia and water content for Blount and Fayette soil clays at 2% and 90% relative humidity.

 





HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
The SCI Journals Agronomy Journal Crop Science
Journal of Natural Resources
and Life Sciences Education
Vadose Zone Journal
Journal of Plant Registrations Journal of
Environmental Quality
The Plant Genome
Copyright © 2005 by the Soil Science Society of America.